Hormesis is a widespread phenomenon across occurring many taxa and chemical
s, and, at the single species level, issues regarding the application of ho
rmesis to human health and ecological risk assessment are similar. However,
interpreting the significance of hormesis for even a single species in an
ecological risk assessment can be complicated by competition with other spe
cies, predation effects, etc. In addition, ecological risk assessments may
involve communities of hundreds or thousands of species as well as a range
of ecological processes. Applying hermetic adjustments to threshold effect
levels for chemicals derived from sensitivity distributions for a large num
ber of species is impractical. For ecological risks, chemical stressors are
frequently of lessor concern than physical stressors (e.g., habitat altera
tion) or biological stressors (e.g., introduced species), but the relevance
of hormesis to non chemical stressors is unclear. Although ecological theo
ries such as the intermediate disturbance hypothesis offer some intriguing
similarities between chemical hormesis and hermetic-like responses resultin
g from physical disturbances, mechanistic explanations are lacking. While f
urther exploration of the relevance of hormesis to ecological risk assessme
nt is desirable, it is unlikely that hormesis is a critical factor in most
ecological risk assessments, given the magnitude of other uncertainties inh
erent in the process.